WO2006120396A2 - Carbone derivatise - Google Patents

Carbone derivatise Download PDF

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Publication number
WO2006120396A2
WO2006120396A2 PCT/GB2006/001643 GB2006001643W WO2006120396A2 WO 2006120396 A2 WO2006120396 A2 WO 2006120396A2 GB 2006001643 W GB2006001643 W GB 2006001643W WO 2006120396 A2 WO2006120396 A2 WO 2006120396A2
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Prior art keywords
carbon
derivatised
amino acid
derivative
cysteine
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PCT/GB2006/001643
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English (en)
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WO2006120396A3 (fr
Inventor
Richard Guy Compton
Gregory George Wildgoose
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Isis Innovation Limited
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Application filed by Isis Innovation Limited filed Critical Isis Innovation Limited
Priority to BRPI0611256-0A priority Critical patent/BRPI0611256A2/pt
Priority to US11/913,762 priority patent/US20080190855A1/en
Priority to EP06743877A priority patent/EP1877343A2/fr
Priority to JP2008509509A priority patent/JP2008542197A/ja
Publication of WO2006120396A2 publication Critical patent/WO2006120396A2/fr
Publication of WO2006120396A3 publication Critical patent/WO2006120396A3/fr

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    • C—CHEMISTRY; METALLURGY
    • C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
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    • C09C1/00—Treatment of specific inorganic materials other than fibrous fillers; Preparation of carbon black
    • C09C1/44—Carbon
    • C09C1/48—Carbon black
    • C09C1/56—Treatment of carbon black ; Purification
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
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    • B01J20/30—Processes for preparing, regenerating, or reactivating
    • B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
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    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01J20/3217—Resulting in a chemical bond between the coating or impregnating layer and the carrier, support or substrate, e.g. a covalent bond
    • B01J20/3219—Resulting in a chemical bond between the coating or impregnating layer and the carrier, support or substrate, e.g. a covalent bond involving a particular spacer or linking group, e.g. for attaching an active group
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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    • B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30—Processes for preparing, regenerating, or reactivating
    • B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3242—Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
    • B01J20/3244—Non-macromolecular compounds
    • B01J20/3246—Non-macromolecular compounds having a well defined chemical structure
    • B01J20/3248—Non-macromolecular compounds having a well defined chemical structure the functional group or the linking, spacer or anchoring group as a whole comprising at least one type of heteroatom selected from a nitrogen, oxygen or sulfur, these atoms not being part of the carrier as such
    • B01J20/3251—Non-macromolecular compounds having a well defined chemical structure the functional group or the linking, spacer or anchoring group as a whole comprising at least one type of heteroatom selected from a nitrogen, oxygen or sulfur, these atoms not being part of the carrier as such comprising at least two different types of heteroatoms selected from nitrogen, oxygen or sulphur
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30—Processes for preparing, regenerating, or reactivating
    • B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3242—Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
    • B01J20/3244—Non-macromolecular compounds
    • B01J20/3246—Non-macromolecular compounds having a well defined chemical structure
    • B01J20/3248—Non-macromolecular compounds having a well defined chemical structure the functional group or the linking, spacer or anchoring group as a whole comprising at least one type of heteroatom selected from a nitrogen, oxygen or sulfur, these atoms not being part of the carrier as such
    • B01J20/3253—Non-macromolecular compounds having a well defined chemical structure the functional group or the linking, spacer or anchoring group as a whole comprising at least one type of heteroatom selected from a nitrogen, oxygen or sulfur, these atoms not being part of the carrier as such comprising a cyclic structure not containing any of the heteroatoms nitrogen, oxygen or sulfur, e.g. aromatic structures
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30—Processes for preparing, regenerating, or reactivating
    • B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
    • B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
    • B01J20/3242—Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
    • B01J20/3268—Macromolecular compounds
    • B01J20/3272—Polymers obtained by reactions otherwise than involving only carbon to carbon unsaturated bonds
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J45/00—Ion-exchange in which a complex or a chelate is formed; Use of material as complex or chelate forming ion-exchangers; Treatment of material for improving the complex or chelate forming ion-exchange properties
    • C—CHEMISTRY; METALLURGY
    • C01—INORGANIC CHEMISTRY
    • C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00—Carbon; Compounds thereof
    • C01B32/05—Preparation or purification of carbon not covered by groups C01B32/15, C01B32/20, C01B32/25, C01B32/30
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00—Treatment of water, waste water, or sewage
    • C02F1/28—Treatment of water, waste water, or sewage by sorption
    • C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
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    • C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09C—TREATMENT OF INORGANIC MATERIALS, OTHER THAN FIBROUS FILLERS, TO ENHANCE THEIR PIGMENTING OR FILLING PROPERTIES ; PREPARATION OF CARBON BLACK  ; PREPARATION OF INORGANIC MATERIALS WHICH ARE NO SINGLE CHEMICAL COMPOUNDS AND WHICH ARE MAINLY USED AS PIGMENTS OR FILLERS
    • C09C1/00—Treatment of specific inorganic materials other than fibrous fillers; Preparation of carbon black
    • C09C1/44—Carbon
    • C09C1/48—Carbon black
    • C09C1/56—Treatment of carbon black ; Purification
    • C09C1/565—Treatment of carbon black ; Purification comprising an oxidative treatment with oxygen, ozone or oxygenated compounds, e.g. when such treatment occurs in a region of the furnace next to the carbon black generating reaction zone
    • C—CHEMISTRY; METALLURGY
    • C01—INORGANIC CHEMISTRY
    • C01P—INDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2002/00—Crystal-structural characteristics
    • C01P2002/80—Crystal-structural characteristics defined by measured data other than those specified in group C01P2002/70
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    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/10—Inorganic compounds
    • C02F2101/103—Arsenic compounds
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00—Nature of the contaminant
    • C02F2101/10—Inorganic compounds
    • C02F2101/20—Heavy metals or heavy metal compounds

Definitions

  • This invention relates to derivatised carbon, in particular to graphite and other forms of carbon having surfaces chemically modified to impart desired properties.
  • Polypeptides such as poly-L-histidine, poly-L-aspartic acid, poly-L-glutamic acid and in particular poly-L-cysteine are known to chelate metal ions such as Cd", Pb", Ni" and Cu” and have been attached to various substrates and used in the trace analysis of these metals (Malachowski et al, Anal. Chim. Acta. 2003, 495, 151; Malachowski et al, Anal. Chim. Acta 2004, 517, 187; Malachowski et al, Pure Appl. Chem. 2004, 76, 777; Johnson et al, Anal. Chem. 2005, 77, 30; Howard et al, J. Anal. At. Spectrom.
  • Biohomopolymers and other peptides possess significant advantages for metal extraction or reclamation over traditional techniques such as simple filtration or precipitation, as the latter are often unable to reduce the concentration of the target metals to meet strict environmental agency regulations.
  • Graphite surfaces can be chemically modified using a variety of relatively facile techniques such as physisorption and chemically or electrochemically initiated chemisorption of a given chemical or biological moiety.
  • Graphite having derivatised surfaces may be used in a variety of applications, for instance as electrode materials in battery technology and as sensors. Although reactive groups such as hydroxy! and carboxyl moieties are known to be present on the surface of graphitic materials, the use of chemically derivatised graphite as a solid-state support for synthetic chemistry applications has been limited.
  • the present invention provides carbon-based solid-state supports upon which to conduct synthetic, step-wise syntheses. This allows the derivatisation of the surface of such materials in a "building-block” fashion, to impart desired properties such as sensitivity to a target analyte.
  • species such as amino acids, peptides, small proteins and nucleic acids can coupled to carbon (e.g. graphite) particles in a relatively facile manner.
  • carbon e.g. graphite
  • the present invention provides derivatised carbon, especially graphite, to which is attached an amino acid or a derivative thereof.
  • the amino acid may be monomer (e.g. cysteine) or a polypeptide (e.g. poly-L-cysteine), which is capable of binding metal ions.
  • the invention is therefore particularly relevant to the detection and removal of toxic heavy metals from water and other liquid media.
  • derivatised carbon in which an amino acid or a derivative thereof is attached to the carbon.
  • the attachment may be direct or indirect, for example via a phenylamine group.
  • the present invention also provides a method of preparing a derivatised carbon in which the carbon is contacted with a nitrobenzenediazonium compound under conditions such that a nitrophenyl-derivatised carbon is produced.
  • the present invention also provides a method of preparing derivatised carbon in which the carbon is attached directly to the amino acid or derivative thereof via carboxyl groups on the surface of the carbon, the method comprising converting carboxyl groups on the surface of the carbon to acyl halide groups and then contacting the resultant product with the amino acid or derivative thereof.
  • the present invention also provides a carbon electrode comprising derivatised carbon of the invention.
  • the invention further provides an electrochemical device including an electrode of the invention.
  • the electrochemical device may be in the form of an electrochemical sensor or reactor.
  • the present invention provides a method of removing metal ions from a liquid medium comprising contacting the medium with derivatised carbon of the invention.
  • the present invention provides a method of detecting the presence of metal ions in a liquid medium comprising subjecting the medium to voltammetric analysis using an electrochemical device of the invention.
  • Derivatised carbon of the invention may be useful in the detection, removal, sequestration and titration of metal ions from liquid media, including water and other aqueous media.
  • metal ions include, for instance, Cd(II), Pb(II), Zn(II), Cu(II) and As(III) ions.
  • the derivatised carbon may be in particulate form, for example in the form of a powder. Particulate materials such as graphite powder and glassy carbon powder are desirable because of their high surface area, which allows them to couple relatively large amounts of amino acids or derivatives thereof. Derivatised carbon of the invention may therefore be able to bind a significantly greater amount of metal ions than known modified solid-state materials.
  • Fig. 1 shows: a) consecutive voltammograms showing the response of 4-nitrophenyl- derivatised carbon (“NPcarbon”) in pH 6.8 buffer; b) overlaid voltammograms of blank graphite powder and aniline-derivatised carbon ("ANcarbon”) in acetonitrile containing 0.1 M tetrabutylammonium perchlorate (TBAP) as supporting electrolyte; and c) consecutive voltammograms showing the response of 4-nitrobenzoic acid- derivatised carbon (“NBANcarbon”) in pH 6.8 buffer.
  • NPcarbon 4-nitrophenyl- derivatised carbon
  • ANcarbon blank graphite powder and aniline-derivatised carbon
  • TBAP tetrabutylammonium perchlorate
  • Fig. 2 shows: a) the N 1s region of the X-ray photoelectron spectroscopy (XPS) spectrum of
  • Fig. 3 shows: a) the wide XPS spectrum of poly-S-benzyl-L-cysteine-derivatised carbon
  • PSBCcarbon poly-L-cysteine-derivatised carbon
  • Fig. 4 shows linear sweep stripping voltammograms for Cd 2+ detection with standard additions of Cd 2+ .
  • the inset shows the corresponding standard addition plot.
  • Fig. 5 shows the cadmium concentration profile remaining in a 10 cm 3 sample of river water (original Cd(II) concentration ca. 1.5 mM) after exposure to 10 mg cysteine methylester-derivatised glassy carbon ("CysMeO-GC").
  • Fig. 6 shows the cadmium concentration profile remaining in a 10 cm 3 sample of mineral water (original Cd(II) concentration 50 ppb) after exposure to 10 mg CysMeO-GC.
  • Fig. 7 shows the copper concentration profile remaining in a 10 cm 3 sample of river water after exposure to 10 mg CysMeO-GC for varying times.
  • Fig. 8 shows the concentration of As(III) remaining after exposure to 10mg of PCcarbon powder, stirred for specified lengths of time.
  • the curve shows a first order exponential decay fitted to the data.
  • Fig. 9 shows the concentration of As(III) remaining after exposure to 10mg of CysMeO- GC powder, stirred for specified lengths of time. The curve shows a first order exponential decay fitted to the data.
  • Fig. 10 shows the concentration of As(III) remaining after exposure to 200mg of CysMeO-GC powder to a 200ppb As(II) solution, stirred for specified lengths of time. The curve shows a first order exponential decay fitted to the data.
  • Fig. 11 shows the concentration of As(III) remaining after exposure to 200mg of CysMeO-GC powder to a 120ppb As(III) solution in a Bangladeshi water sample, stirred for specified lengths of time.
  • the curve shows a first order exponential decay fitted to the data.
  • Fig. 12 shows anodic stripping voltammograms of a 120ppb As(III) Bangladeshi water sample exposed to 200mg of CysMeO-GC spherical powder and stirred for 30 minutes.
  • Linear sweep voltammetry (LSV) was performed at 100mV/s, and standard additions of 2.4 x10 "7 M were used.
  • Fig. 13 shows an XPS spectrum of L-cysteine methyl ester-modified carbon powder ("CysOMe-carbon").
  • Fig. 14 shows an baseline-corrected XPS spectrum of CysOMe-carbon powder after exposure to As'" showing the region of interest from 120 to 260 eV.
  • the dotted lines show the Gaussian peak fitting performed using the MicroCal Origin software package.
  • Fig. 15 shows overlaid concentration-time profiles for the removal of Cd" from a ca. 55 ⁇ M solution of Cd(NO 3 ) 2 in pH 5.0 acetate buffer comparing the efficacy of CysOMe-GC and CysOMe-carbon powder adsorbents.
  • Fig. 16 shows a concentration-time profile for the removal of trace amounts of As'" to below the WHO recommended limit of 10 ppb.
  • Fig. 17 shows overlaid Cd" linear sweep anodic stripping voltammetry (LSASV) voltammograms with increasing 1 ⁇ M standard additions of Cd" (0-20 ⁇ M).
  • the inset shows the corresponding standard addition plot.
  • Fig. 18 shows overlaid As 1 " LSASV voltammograms with increasing 0.22 ⁇ M standard additions of As" 1 (0 to 2.2 ⁇ M). The inset shows the corresponding standard addition plot. Description of Various Embodiments
  • the invention provides derivatised carbon to which is attached an amino acid or a derivative thereof.
  • the amino acid or derivative may be attached directly or indirectly (i.e. via a linker) to the carbon.
  • a linker i.e. via a linker
  • carbon to which the amino acid or derivative is attached via a carboxyl or phenylamine group present on the carbon.
  • the amino acid is a sulfur-containing amino acid, for instance, cysteine, glutathione, tyrosine or a derivative thereof.
  • the sulphur-containing amino acid may have pendant thiol or thiol-like groups.
  • the amino acid may be in the form of an ester, e.g. a methyl or ethyl ester, a particular example being L-cysteine methyl ester.
  • Derivatives of amino acids include oligomers and polymers of amino acids.
  • a cysteine derivative may be polycysteine or cysteamine
  • a glutathione derivative may be polyglutathione.
  • An exemplary polymeric amino acid is an S-benzyl protected homopolymer containing 50 to 100 cysteine residues per polymer chain.
  • the amino acid, or derivative thereof, may be protected or unprotected, an example being a polycysteine such as poly-S-benzyl-L-cysteine.
  • the carbon may be in particulate form, for example in the form of a powder.
  • a particulate carbon may comprise particles having a diameter of between 1 and 100 ⁇ m, e.g. between 2 and 50 ⁇ m.
  • graphite powder glassy carbon spherical powder and pyrolytic graphite forms.
  • the carbon may be in the form of carbon nanotubes, for instance, multiwalled carbon nanotubes (MWCNTs).
  • MWCNTs multiwalled carbon nanotubes
  • Examples of derivatised carbons of the invention include glassy carbon modified with cysteine, glutathione or cysteamine or a derivative thereof, and a carbon powder modified with polycysteine or polyglutathione. It will be appreciated that the invention extends to other amino acid polymers and derivatives and also to monomers of amino acids and their thiol-containing derivatives, such as cysteine, coupled to glassy carbon. Particular examples include carbon powder (e.g. graphite powder or glassy carbon spherical powder) derivatised with cysteine or a derivative thereof (e.g. an ester of cysteine such as cysteine methyl ester, or a polymer of cysteine such as polycysteine or poly-S-benzyl-L-cysteine).
  • carbon powder e.g. graphite powder or glassy carbon spherical powder
  • derivatised with cysteine or a derivative thereof e.g. an ester of cysteine such as cysteine methyl ester
  • the derivatised carbon may be obtained by contacting carbon with a nitrobenzenediazonium compound under conditions such that a nitrophenyl-derivatised carbon is produced.
  • the reaction may be carried out in the presence of a suitable reagent such as hypophosphorous acid.
  • the nitrophenyl-derivatised carbon may be reduced to form an aniline-derivatised carbon.
  • the product may be further reacted to produce a substituted aniline-derivatised carbon.
  • the aniline-derivatised carbon may be reacted with an amino acid or derivative thereof (e.g. a polycysteine such as poly-S-benzyl-L-cysteine).
  • Derivatised carbon may also be obtained by converting carboxyl groups present on the surface of a carbon to acyl halide groups and then contacting the resulting product with an amino acid or derivative thereof.
  • the acyl halide may be, for example, acyl chloride. Any carboxyl groups present on the amino acid or derivative thereof may be protected.
  • Derivatised carbon of the invention may be used in the detection (e.g. the electrochemical detection), titration or removal of metal ions from liquid media.
  • the metal ions may be, for instance, one or more of Cd(II), Pb(II), Zn(II), Cu(II) and As(III) ions.
  • the liquid medium may be, for instance, an aqueous medium.
  • Derivatised carbon of the invention may be useful in the detection of arsenic.
  • the carbon may be provided in a relatively expensive drinking water filtration device.
  • a derivatised carbon of the invention is selective for metal ions other than As(III), it may be incorporated into an arsenic sensor in order to remove ions such as Cu(II), which interfere in As(III) detection.
  • the invention may provide inexpensive and attractive materials for use in water clean-up, the recovery or extraction of metals from effluents, and drinking water filtration, where natural supplies are often contaminated by toxic heavy metals such as arsenic and cadmium.
  • the invention further provides materials which may be useful in metal sequestration.
  • polycysteine anchored on carbon typically has a much higher metal uptake (per gram of material) than known substrates such as glass, polymer beads and the like.
  • the density of sequestration units per surface area may also be much greater than for prior art substrates where nano-scale modification is used (e.g. in the case of nanotubes) is used, due to an increase in active surface area.
  • both the thermodynamics and the kinetic rate of metal ion uptake may be enhanced.
  • the present invention provides a solid-state support material in which the support is provided by coupling a biohomopolymer, in particular a polypeptide selected from poly-L-histidine, poly-L-aspartic acid, poly-L-glutamic acid and especially poly-L- cysteine, to graphite powder.
  • a biohomopolymer in particular a polypeptide selected from poly-L-histidine, poly-L-aspartic acid, poly-L-glutamic acid and especially poly-L- cysteine
  • graphite powder are known to chelate toxic heavy metals such as cadmium, lead, nickel and copper with very little affinity for alkali and alkaline earth metals such as sodium and calcium.
  • a cysteine-, poly-L- cysteine-derivatised graphite powder of the invention may be used to quantitatively titrate metal ions, such as Cd(H) ions, from aqueous media.
  • cysteine- or polycysteine-modified carbon may chelate far greater amounts of Cd(II) ions than poly-L-cysteine attached to any other solid-state support material.
  • derivatised carbon of the invention is particularly suited for use in toxic heavy metal recovery from industrial effluents, environmental cleanup and drinking water filtration.
  • Solutions of known pH in the range pH 1.0 to pH 12.0 were prepared in deionised water as follows: pH 1.0, 0.10 M HCI; pH 1.7, 0.1 M potassium tetraoxalate; pH 4.6, 0.10 M acetic acid + 0.10 M sodium acetate; pH 5.04, 0.5 M sodium acetate; pH 6.8, 0.025 M Na 2 HPO 4 + 0.025 M KH 2 PO 4 ; pH 9.2, 0.05 M disodium tetraborate; pH 10.5, 0.1 M disodium tetraborate; and pH 12.0, 0.01 M sodium hydroxide. These solutions contained in addition 0.10 M KCI as supporting electrolyte. pH measurements were performed using a Hanna pH213 pH meter.
  • Electrochemical measurements were recorded using a ⁇ Autolab computer controlled potentiostat (Ecochemie) with a standard three-electrode configuration. Electrochemical experiments were carried out in a glass cell of volume 25cm 3 . Either a basal plane pyrolytic graphite electrode (bppg, 5mm diameter, Le Carbone) or boron doped diamond electrode (BDD, 3mm diameter, Windsor Scientific Ltd.) electrode acted as the working electrode. A platinum coil (99.99%, Goodfellow) acted as the counter electrode. The cell assembly was completed using a saturated calomel electrode (SCE, Radiometer) as the reference electrode unless otherwise stated. All electrochemical experiments were carried out after degassing the solution using pure N 2 gas (BOC gases) for 30 minutes and were conducted at 20 ⁇ 2 0 C.
  • BOC gases pure N 2 gas
  • XPS X-ray photoelectron spectroscopy
  • the sample surface was bombarded with an electron beam (10 eV) from a "flood gun" within the spectrometer's analysis chamber. Analysis of the resulting spectra was performed using Microcal Origin 6.0. Assignment of spectral peaks was determined using the UKSAF and NlST databases.
  • Scheme 1 illustrates synthetic routes for derivatising graphite powder showing the principle behind the "building-block” chemistry and the coupling of poly-L-cysteine to graphite powder:
  • NPcarbon powder (1.02 g) and tin (1.63 g, 13.7 mmol) were suspended in water (12 ml_). Concentrated hydrochloric acid (4.5 ml, 53.8 mmol) was added and the mixture heated to reflux. The reaction mixture was stirred at 100 0 C under an atmosphere of argon. After 18 h the mixture was filtered and the solid washed with hydrochloric acid (100 ml_ of a 1M aqueous solution), methanol (100 ml_), potassium hydroxide (50 ml_ of a 1M aqueous solution) and methanol (50 ml_). The solid was dried in vacuo to afford a black powder (180.4 mg) of the reduced form of NPcarbon consisting of p-aniline moieties covalently derivatised to the graphite surface ("ANcarbon").
  • ANcarbon graphite surface
  • ANcarbon 500 mg
  • 1-hydroxybenzotriazole hydrate HOBt, 670 mg, 5.0 mmol
  • benzotriazol-1-yl-oxytripyrrolidinophosphonium hexafluorophosphate PyBop, 2.6 g, 5 mmol
  • p-nitrobenzoic acid 840 mg, 5 mmol
  • DMF 8 mL
  • Ethyl diisopropylamine U mL, 10 mmol
  • Fig. 1a shows the voltammetry of NPcarbon at pH 6.8.
  • a large reduction wave was observed at ca. -0.685 V vs. SCE labelled as "System I" in Fig. 1a.
  • System I System I
  • System I corresponds to the chemically and electrochemically irreversible reduction of the nitro group in a four-electron, four-proton process to form the arylhydroxylamine. This then undergoes an electrochemically almost-reversible two- electron, two-proton oxidation (System II) to form the arylnitroso species.
  • System II electrochemically almost-reversible two- electron, two-proton oxidation
  • ANcarbon was further characterised using XPS.
  • Fig. 2a shows that a single peak is observed in the N 1s region of the spectrum with a binding energy of 400.1 eV consistent with an aromatic amine moiety. No signals at binding energies corresponding to photoelectrons emitted from the N 1s or O 15 levels within a nitro moiety were observed.
  • Fig. 1c Voltammetric characterisation of the NBANcarbon revealed that the expected characteristic reduction of the nitro group is once again observed and that the voltammetry corresponds to a surface bound species (Fig. 1c).
  • Fig. 2b shows the N 15 region of the XPS spectrum of NBANcarbon. Two peaks are observed with binding energies of 400.6 eV and 405.4 eV and an almost 1:1 ratio of peak heights. Comparison with XPS databases confirms that these peaks correspond to nitrogen atoms in the amide and nitro groups respectively. Furthermore, Gaussian deconvolution of the O 1s region of the spectrum (not shown) reveals peaks with binding energies of 530.7 eV and
  • Figs. 3a and 3b show the resulting XPS spectra for PSBCcarbon and PCcarbon respectively.
  • Two peaks with binding energies of 162.5 eV and 226.5 eV corresponding to photoelectrons emitted from the S 2p3 ⁇ 2 and the S 2s levels were observed in the PSBCcarbon in excellent agreement with literature values for S-benzyl protected polycysteine.
  • the binding energies of the S 2p3/2 and the S 2s photoelectrons were shifted slightly to 163.5 eV and 227.5 eV, again in excellent agreement with literature values for the free thiol in polycysteine.
  • Example 2 Quantitative analysis of cadmium in aqueous media using PCcarbon
  • the optimised pH for Cd 2+ detection is pH 5 and therefore a 0.05M sodium acetate buffer (pH 5.04) was used for both the chelation of Cd 2+ by the PCcarbon and the LSV detection of the amount of Cd 2+ chelated.
  • the LSV protocol for cadmium detection involved depositing the Cd 2+ on the BDD electrode as Cd 0 by holding the potential at -1.5 V vs. SCE for 60s whilst stirring the solution. LSV was then carried out by scanning the potential from -1.1 V to -0.3 V at 100 mVs "1 and a cadmium stripping peak observed at ca. -0.8 V vs. SCE. To verify the accuracy of this protocol, a "blind" solution of Cd(NO 3 ) 2 was analysed by standard additions of 5 nM Cd 2+ and a standard addition plot of peak height vs. Cd 2+ concentration constructed.
  • Fig. 4 shows the overlaid resulting LSV voltammograms for increasing amounts of Cd 2+ and the resulting standard addition plot (inset).
  • the Cd 2+ concentration was determined by the LSV protocol to be 20.5 nM ⁇ 0.1 nM with a limit of detection (3 ⁇ ) of 0.2 nM.
  • the actual Cd 2+ concentration was 20 nM ⁇ 0.1 nM demonstrating that the LSV protocol was an accurate method for trace Cd 2+ determination over the concentration range 1-100 nM.
  • Table 1 shows the amount of Cd 2+ chelated for varying masses of PCcarbon. The experiments were repeated with the length of time the PCcarbon was stirred with Cd 2+ varied from ten minutes to 12 hours. Increasing the exposure time of Cd 2+ to PCcarbon was not found to increase the amount of Cd 2+ chelated. A similar experiment was carried out with blank graphite powder for comparison. The uptake of Cd 2+ by blank graphite powder was not measurable. From the results presented in Table 1 it was possible to calculate that PCcarbon chelates 1218 ⁇ mol ⁇ 200 ⁇ mol of Cd 2+ per gram of PCcarbon.
  • Cd 2+ can be quantitatively recovered from polycysteine using nitric acid as a result of tertiary conformational changes, rather than simple proton exchange with the thiol groups (Howard et al, J. Anal. At. Spectrom., 1999, 14, 1209; and Miller et al, Anal. Chem., 2001, 73, 4087).
  • Cadmium ions were recovered from the PCcarbon by stirring the filtered PCcarbon samples in 1M HNO 3 . After stirring each sample of PCcarbon in 10 cm 3 1.0 M HNO 3 for either 30 minutes or 5 hours, the suspension was filtered.
  • 4-Nitrophenyl groups were coupled to graphite and MWCNTs via the diazonium salt chemistry described in Example 1.
  • the nitro group was reduced with Sn/HCI to produce aniline-modified carbon and MWCNTs.
  • the aniline group was then diazotised and coupled to tyrosine to produce a material capable of metal chelation and also a route for further coupling amino acid- or thiol-containing molecules to the tyrosine-modified carbon and MWCNTs.
  • the amine groups of the aniline moieties on the surface of the derivatised carbon and MWCNTs were also converted to thiol groups, for use in metal chelation/recovery.
  • LSV linear sweep voltammetry
  • LSV detection of Cd(II) was carried out using the following parameters: a 10 ⁇ L aliquot of the sample to be tested was added to 10 cm 3 of the sodium acetate buffer. Cadmium was deposited onto the BDD electrode at a potential of -1.5 V vs. SCE, for 60 s with stirring. The potential was then swept at 100 mVs "1 from -1.1 V to -0.6 V vs. SCE with a cadmium stripping peak observed at ca. -0.780 V vs. SCE. Standard additions of 0.1 ⁇ M
  • Fig. 5 shows the resulting Cd(II) concentration profile. It is apparent that ca. 87% of the Cd(II) was removed from the sample by 10 mg of CysMeO-GC powder. The residual Cd(H) concentration was approximately half that of the calculated drinking water concentration of Cd(II) in the St Russia water supply out of the tap, which is still above the WHO, EU and EPA guidelines. CysMeO-GC powder may be used as a cheap and highly effective material for use in environmental clean up and/or metal ion sequestration.
  • Cys-GC is therefore an excellent material for use in drinking water filtration to remove toxic heavy metals such as Cd(II).
  • SWV stripping protocol used was based on a previous detection protocol (Banks et al, Phys. Chem. Chem. Phys., 2003, 5, 1652).
  • a 50 ⁇ m diameter gold disc electrode ( ⁇ 99.99%, Goodfellow) was used as the working electrode, with a platinum coil and saturated calomel electrode (SCE, Radiometer) acting as counter and reference electrodes respectively.
  • SCE saturated calomel electrode
  • the electrochemical experiments were carried out using a computer controlled potentiostat ( ⁇ Autolab) in pH 2.00 0.1 M phosphoric acid (H 3 PO 4 ) buffer with 0.1 M KCI added as supporting electrolyte.
  • SWV detection of Cu(II) was carried out using the following parameters: frequency 50 Hz, step potential 2 mV, amplitude 25 mV.
  • a 0.5 cm 3 aliquot of the sample to be tested was added to 9.5 cm 3 of the phosphoric acid buffer. Copper was deposited onto the working electrode at a potential of -1.5 V vs. SCE, for 15 s with stirring. The potential was then swept -1.0 V to +0.6 V vs. SCE with a copper stripping peak observed at ca. -0.05 V vs. SCE. Standard additions of 1.0 ⁇ M Cu(II) were then added over the range 1.0-10.0 ⁇ M and a corresponding addition plot was constructed and used to calculate the background Cu(II) concentration in the original sample.
  • a 10 cm 3 sample of River Cherwell water (untreated) was analysed using the SWV copper stripping protocol outlined above and found to have a Cu(II) concentration of ca. 30 ⁇ M which is just above the EPA limit fo 1.3 mg L "1 or 20.1 ⁇ M and was therefore used without spiking the Cu(II) concentration.
  • the sample was exposed to 10 mg of CysMeO-GC and analysed at various intervals for one hour to measure the remaining Cu(II) concentration.
  • Fig. 7 shows the resulting removal of Cu(II) from the sample.
  • Voltammetric measurements were carried out using a ⁇ -Autolab III (ECO-Chemie) potentiostat. All measurements were conducted using a three electrode cell.
  • the working electrode was a gold micro disk electrode (1mm diameter), which was constructed in house by sealing a gold wire into Teflon housing.
  • the counter electrode was a bright platinum wire, with a saturated calomel electrode (Radiometer) as the reference.
  • the gold electrode was polished using a 0.1 ⁇ m alumina slurry on a soft lapping pad.
  • the working electrode was placed in a face-on arrangement to the ultrasonic horn and the horn was immersed beyond the shoulder of the stepped tip to ensure that ultrasound was efficiently applied to the solution.
  • the voltammetric curves were baseline corrected using autolab software, which utilises a third-order polynomial correction.
  • a 1.1 mM solution of As(III) was prepared from sodium (meta) arsenite dissolved in ultra pure water at pH 5.4 , 25 mL of the solution was placed in a stirred flask to which 10 mg of the polycysteine carbon powder (PCcarbon) was added. At intervals of 10,30 and 60 minutes, a 50 ⁇ L sample was taken from the solution, which was then diluted down into 0.1 M nitric acid to trace levels for analysis. The analysis was performed by holding the gold electrode at -0.6 V (vs. SCE) for 60s, ultrasound was used during this period at a horn to tip distance of 20 mm and an amplitude of 5 %. The potential was then swept positively to 1 V (vs.
  • Fig. 8 shows the reduction in As(III) concentration over time, after 60 minutes of stirring the concentration of As(III) has dropped from 1.1 mM to 0.7 mM a 36 % decrease, a first order exponential decay line has been fitted through the points. The solution was then left for a period of 20 days without further stirring after this time the concentration was found to have dropped to 0.55 mM.
  • a 0.98 mM solution of As (III) was prepared from sodium (meta) arsenite dissolved in ultra pure water at pH 5.4, 25 mL of the solution was placed in a stirred flask to which 10 mg of the Cys-GC powder was added. At intervals of 10, 20 and 60 minutes, a 50 ⁇ L sample was taken from the solution which was then diluted down in 0.1 M nitric acid to trace levels for analysis.
  • Fig. 9 shows the reduction in As(III) concentration over time, after 60 minutes of stirring the concentration of As(III) has dropped from 0.98 mM to 0.7 mM a 28.6 % decrease. The solution was then left 3 days without further stirring however no further decrease in arsenic concentration was found after this time.
  • Fig. 10 shows that after only ten minutes the arsenic concentration has been significantly reduced from 200 ppb to 77 ppb, and after 30 minutes the level has dropped to 55 ppb. Analysis at 60 minutes shows that the concentration of arsenic has remained constant at this level (a 73 % decrease) leaving the concentration of As(III) present just above the Bangladeshi safe drinking limit.
  • a real sample was then used to test the ability of the CysMeO-GC powder to complex arsenic in an authentic Bangladeshi well water sample.
  • the sample was first tested by the ASV method to determine the concentration of As(III) present. However, the concentration of As(III) was found to be below the detectable limit (1x10 "8 M), and so the water sample was spiked to a value of 120 ppb for use in the experiments.
  • 200 mg of the CysMeO-GC powder was added to 25 mL of the water sample which was then stirred for a specified time (5, 10, 30 and 45 minutes), before being filtrated to remove the powder from the solutions. Once again the sample was diluted 1:1 into 0.1 M nitric acid for the analysis experiments.
  • Fig. 11 shows the results of the analysis fitted to a first order exponential decay. After only 5 minutes of stirring the concentration of arsenic present had dropped by 47% to 64 ppb, at 10 minutes the concentration is found to have dropped further by 69% to 38 ppb (i.e. 12 ppb below the Bangladeshi safe drinking limit). After 45 minutes, the drop in concentration has levelled off at 34 ppb, or 28 % of the original value. As the analysis was conducted in a real sample rather than pure water the experiment was exposed to many trace metals generally found in Bangladeshi water supplies (copper, lead, mercury etc; Anawar et al, Environment International 2002, 27, 597).
  • Fig. 12 shows the ASV plots from the analysis of the 30 minute sample, a large stripping wave can be seen at approximately 0.4 V vs. SCE, due to one of these contaminants.
  • reagents were purchased from Aldrich, with the exception of the glassy carbon microspherical powder (Alfa Aesar, Type I, diameter 10-20 ⁇ m) and potassium chloride (Reidel de Haen) and were of the highest commercially available grade and used without further purification. All aqueous solutions were prepared using deionised water with a resistivity not less than 18.2 M ⁇ cm (Vivendi Water Systems). pH measurements were performed using a Hanna Instruments pH213 pH meter.
  • the sample surface was bombarded with an electron beam (10 eV) from a "flood gun" within the analysis chamber of the spectrometer. Note that the peak positions reported have not been corrected relative to the C 1s literature value of 286.6 eV to account for the effect of the flood gun on the peak positions of spectral lines. Analysis of the resulting spectra was performed using MicroCal Origin 6.0. Assignment of the spectral peaks was made using the UKSAF and NIST databases.
  • the percentage surface elemental composition was calculated from the areas under each peak in the wide spectrum adjusted by each elements individual X-ray cross- sectional area. Taking into account the relevant atomic sensitivity factors for the various elements it was found that the CysOMe comprises ca. 10% of the surface elements with a variation between different sample preparations of ⁇ 3%. This surface coverage is in good agreement with that obtained using combustion analysis which gave a surface coverage of CysOMe as being 10-14% and is approximately twice that for CysOMe-GC powder. XPS analysis was also performed on samples of the CysOMe-carbon powder after exposure to either Cu", Cd" or As 1 " solutions for sufficient times for the uptake of metal ions to be complete (see sections below). Fig.
  • Example 9 Detection and removal of various metal ions using CvsOMe-carbon powder
  • Electrochemical measurements were performed using a ⁇ -Autolab computer controlled potentiostat (EcoChemie).
  • a three electrode cell with a solution volume of 10 cm 3 was used throughout.
  • the working electrode consisted of either a glassy carbon (GC, 3mm diameter, BAS), a square boron doped diamond electrode (BDD, 3mm x 3mm, Windsor Scientific Ltd) or gold (1mm diameter, GoodFellow) macrodisc electrode.
  • a bright platinum wire (99.99% GoodFellow) acted as the counter electrode and either a silver wire pseudo-reference electrode (99.99% GoodFellow) or a saturated calomel electrode reference electrode (SCE, Radiometer) completed the three-electrode assembly. All solutions were degassed using pure N 2 (BOC Gases) for 20 minutes prior to any electrochemical experiment being performed.
  • Inductively coupled plasma atomic emission spectroscopic (ICPAES) determination of As"' concentration in solution was analysed with the Perkin Elmer Optima 5300DV emission ICP instrument.
  • the recommended emission wavelength was 188.979nm and axial view is recommended for the best detection. As this is below the 200nm threshold the optics were purged at a high flow of argon to minimise any absorption of light by water and air.
  • the As"' calibration using 5 points (0, 50, 100, 150, 200ppb), gave a correlation coefficient 0.9993, and the limit of detection, defined as 3 times the standard deviation of the blank, averaged from 4 blank checks each measured in 3 replicates, was found to be 9.78ppb or 0.0098ppm.
  • the Perkin Elmer expected value is 1 to 10ppb for this wavelength so the sensitivity is acceptable.
  • the blank check solutions gave between 2.0 and 4.5ppb for 4 checks.
  • thermodynamic parameters K' and n
  • K' and n are Freundlich constants relating to the maximum adsorption capacity; the larger the value of K' and the smaller the value of n, the higher the affinity of the adsorbent towards the adsorbens.
  • the uptake of As 1 " ions by CysOMe-carbon powder was measured as follows. 40mg of the modified carbon powder was stirred in 20 cm 3 solution containing varying concentrations (10 to 150 ⁇ M) of arsenic for varying times ranging from a few minutes to several hours. The powder was then filtered off and the solution analysed using LSASV to determine the concentration of As'" remaining. A set of samples that had been analysed by the LSASV method were then analysed for their As 1 " concentration using ICP-AES. The results of the ICP-AES analysis were found to be in good agreement (within 5%) with those obtained by LSASV, demonstrating that the electroanalytical protocol produced accurate and reliable results.
  • the concentration of Cd" remaining in a sample after exposure to CysOMe-carbon powder was determined using a LSASV protocol at a boron doped diamond electrode
  • BDD Banks et al
  • pH 5.0 sodium acetate buffer pH 5.0 sodium acetate buffer.
  • LSASV analysis was carried out using the following parameters: the BDD electrode was held at a deposition potential of -1.5 V vs. SCE for 60 seconds with stirring. The potential was then swept from -1.2 V to -0.1 V vs. SCE at a scan rate of 0.1 Vs "1 . A cadmium stripping peak was observed at ca. -0.8 V vs. SCE.
  • Standard 1 ⁇ M Cd" additions were then added to the sample being analysed and the unknown Cd" concentration was determined by constructing a standard addition plot, as shown in Fig. 17. The analysis was repeated three times and the Cd" concentration remaining in the sample was calculated as the average of the three results.
  • the Cu” concentration in a sample was determined using the standard addition method described above and an LSASV protocol using the following protocol.
  • Cu analysis was performed in 0.1 M H 3 PO 4 , pH 2.0, using a GC working electrode and a Ag pseudo- reference electrode to avoid the formation of copper(l) chloride precipitates during the electrodeposition (which could otherwise form if a SCE reference electrode was used and are problematic for the LSASV analysis).
  • a copper stripping peak could be observed at ca. -0.1 V vs. Ag.
  • the linear analytical concentration range, using standard additions of 1 ⁇ M Cu was found to be 2 to 20 ⁇ M; therefore all samples were diluted to fall within this range where necessary.
  • LSASV was performed using a deposition potential of -1.5 V vs. Ag, deposition time 30s, scan rate 100 mVs "1 and scanning from - 1.5 Vto +0.8 V vs. Ag.
  • LSASV was performed in a solution, 10 cm 3 in volume, of 0.1 M HCI (pH 1.0) using a gold working electrode (diameter 1mm) with a SCE acting as the reference electrode.
  • the LSASV analysis was carried out on samples of relatively high concentration using the following parameters: deposition potential -0.3 V vs. SCE, deposition time 60s with stirring for the first 5 s.
  • LSASV voltammetry was performed from -0.3 V to +0.4 V vs. SCE at 100 mVs "1 , step potential 5 mV. Standard 2.2 ⁇ M additions (5 ⁇ L of a 4.4 mM standard solution) were then added, and the unknown sample concentration determined form a standard addition plot.
  • the linear range for As'" detection was found to be 2 to 20 ⁇ M with a limit of detection (based on the 3 ⁇ value) of 1.25 ⁇ M. Where necessary, solutions were diluted so that their concentration fell within this range prior to analysis.
  • the protocol was modified slightly. The solution was stirred throughout the entire 60s deposition time with all other parameters identical to those described above.
  • the standard As"' solution was diluted so that a 5 ⁇ L aliquot added to the analysis sample corresponded to a 0.22 ⁇ M standard addition and the resulting voltammetry is shown in Fig. 18.
  • the linear range was determined to be 0 to 2.2 ⁇ M with a limit of detection of 0.03 ⁇ M therefore it was not necessary to dilute the samples prior to analysis.

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Abstract

L'invention concerne un carbone dérivatisé dans lequel un amino-acide ou son dérivé sont fixés au carbone. Le carbone dérivatisé décrit dans l'invention peut être utile pour détecter et éliminer des ions métalliques d'un milieu liquide.
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US8197650B2 (en) 2007-06-07 2012-06-12 Sensor Innovations, Inc. Silicon electrochemical sensors
CN102590320A (zh) * 2012-02-03 2012-07-18 中国科学院长春应用化学研究所 巯基乙胺修饰电极用于检测痕量三价无机砷的电化学方法
US8758584B2 (en) 2010-12-16 2014-06-24 Sensor Innovations, Inc. Electrochemical sensors
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US10287184B2 (en) * 2016-11-16 2019-05-14 University Of Dammam Water filtration apparatus and a method of using thereof
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US8506779B2 (en) 2007-06-07 2013-08-13 Sensor Innovations, Inc. Electrochemical sensors
WO2009147244A1 (fr) * 2008-06-06 2009-12-10 Ecole Polytechnique Procédé et dispositif utilisant une membrane nanoporeuse pour détecter et quantifier des métaux lourds dans un fluide par voltamétrie par strippage anodique
US9134267B2 (en) 2008-06-06 2015-09-15 Ecole Polytechnique Method and device using nanoporous membrane for detecting and quantifying heavy metal ions in a fluid by anodic stripping voltammetry
US8758584B2 (en) 2010-12-16 2014-06-24 Sensor Innovations, Inc. Electrochemical sensors
CN102590320A (zh) * 2012-02-03 2012-07-18 中国科学院长春应用化学研究所 巯基乙胺修饰电极用于检测痕量三价无机砷的电化学方法
US10323331B2 (en) 2016-12-29 2019-06-18 Industrial Technology Research Institute Valuable metal selectively adsorbing electrode and method for selectively recovering valuable metals

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